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EP0976718A2 - Improved nitration process - Google Patents

Improved nitration process Download PDF

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Publication number
EP0976718A2
EP0976718A2 EP99114369A EP99114369A EP0976718A2 EP 0976718 A2 EP0976718 A2 EP 0976718A2 EP 99114369 A EP99114369 A EP 99114369A EP 99114369 A EP99114369 A EP 99114369A EP 0976718 A2 EP0976718 A2 EP 0976718A2
Authority
EP
European Patent Office
Prior art keywords
gases
aromatic compound
nitric acid
nitrator
nitratable
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
EP99114369A
Other languages
German (de)
French (fr)
Other versions
EP0976718A3 (en
EP0976718B1 (en
Inventor
Clive M.H. Brereton
Alfred A. Guenkel
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Noram International Ltd
Original Assignee
Noram Engineering and Constructors Ltd
Noram International Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Noram Engineering and Constructors Ltd, Noram International Ltd filed Critical Noram Engineering and Constructors Ltd
Publication of EP0976718A2 publication Critical patent/EP0976718A2/en
Publication of EP0976718A3 publication Critical patent/EP0976718A3/en
Application granted granted Critical
Publication of EP0976718B1 publication Critical patent/EP0976718B1/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C201/00Preparation of esters of nitric or nitrous acid or of compounds containing nitro or nitroso groups bound to a carbon skeleton
    • C07C201/06Preparation of nitro compounds
    • C07C201/08Preparation of nitro compounds by substitution of hydrogen atoms by nitro groups

Definitions

  • This invention relates to an improved continuous process for the nitration of nitratable organic compounds and particularly for the preparation of mononitrobenzene (MNB) from benzene utilizing nitric acid and sulfuric acid feed stocks.
  • MNB mononitrobenzene
  • nitrous oxide (NO x ) gases produced in the nitration process are collected in water under pressure to produce weak nitric acid which is recycled to the nitric acid feed stock.
  • Nitrated aromatic hydrocarbons and nitrated halogenated aromatic hydrocarbons and particularly mononitrobenzene are important chemical intermediates.
  • Guenkel et al, United States Patent No. 5,313,009 (the '009 patent), assigned to the assignee of the present invention describes a continuous process to nitrate a nitratable aromatic compound, typically an aromatic hydrocarbon or a halogenated aromatic hydrocarbon, and particularly benzene, in which the formation of oxidation by-products is substantially reduced compared with the prior art and wherein the reaction rate is substantially increased.
  • a nitratable aromatic compound typically an aromatic hydrocarbon or a halogenated aromatic hydrocarbon, and particularly benzene
  • NO x gases are still formed which preferably are not released into the atmosphere for environmental reasons.
  • the prior art has suggested treating these NO x gases with a caustic solution to form sodium nitrite or sodium nitrate salts, which are disposed of as the salt.
  • Small quantities of CO 2 are also formed in the nitration process. CO 2 will react with sodium hydroxide to form sodium carbonate; this increases the consumption of sodium hydroxide.
  • the use of sodium hydroxide and formation of salts which must be subsequently disposed of is not completely acceptable on an industrial basis.
  • the discharge of nitrates and especially nitrites of sodium is facing increasingly strict regulation.
  • the present invention describes a system for removal of NO x gases which can be utilized in conjunction with the nitration process disclosed in the aforesaid '009 patent, as well as other nitration processes where NO x gases are formed to efficiently and effectively convert the NO x gases into weak nitric acid, preferably recycled to the nitric acid feed stock.
  • the present invention provides a continuous nitration process of an aromatic compound such as benzene utilizing nitric acid and sulfuric acid feed stocks wherein NO x gases produced in the process are contacted with water under pressure and converted to weak nitric acid which is recycled to the nitric acid feed stock.
  • NO x gases are collected from strategic areas of the nitrating system, contacted with air and water, for example, in a packed bed unit at elevated temperature and pressure whereby the NO x gases are absorbed by the water to form weak nitric acid.
  • the weak nitric acid is recovered from the packed bed unit and recycled to the nitric acid feed stock.
  • CO 2 is not absorbed in a NO x scrubber if the scrubber is operated in an acidic mode. Clean NO x free vent gas is vented from the packed bed unit.
  • the system is not only effective and efficient, but additionally is cost saving in that the NO x gases being recovered as nitric acid are reused in the nitration process.
  • a pipe nitrator 100 receives concentrated sulfuric acid from conduit 102, nitric acid from conduit 104 and hydrocarbon, i.e., benzene, to be nitrated from conduit 106.
  • the acid streams are blended in a ratio such that the resulting mixed acid contains nitric acid mostly in the form of reactive species, i.e., the nitronium ion as described in the '009 patent.
  • the two acid streams from conduits 102 and 104 may be mixed in line before entering the pipe nitrator 100 or they may be introduced separately into the pipe nitrator 100.
  • the pipe nitrator 100 discharges to a stirred tank type nitrator 112.
  • the reaction rate is very fast, which is specific to the hydrocarbon species to be nitrated and specific to the operating conditions, the reaction may go essentially to completion inside the pipe nitrator 100 so that the stirred tank type of nitrator 112 is not required.
  • the pipe nitrator 100 serves mainly as a hydrocarbon dispersion device. Fresh nitrating acid enters the stirred tank nitrator 112 and intimately mixes with fresh hydrocarbon.
  • the process fluids pass to a separator 114 and the nitro product compound is discharged from separator 114 through conduit 116 and fed to a product wash and effluent treatment system 124.
  • Pure nitro organic product i.e., mononitrobenzene when benzene is treated, is recovered at conduit 125, aqueous effluent is discharged through conduit 126 and some organic recycle is fed by line 127 to hydrocarbon feed 106.
  • Spent sulfuric acid recovered from separator 114 is delivered to a sulfuric acid concentrator 118.
  • water is removed via conduit 120 which is fed to a vacuum system 123 while reconcentrated sulfuric acid is recycled to the pipe nitrator 100 through conduit 117.
  • NO x gases are drawn off in vacuum system 123 and collected through line 128 at head unit 121. Condensate from vacuum system 123 is fed to product wash and effluent treatment system 124 where additional NO x gases are drawn off and fed to head unit 121 through a second line 128. Finally, additional NO x gases are vented from separator 114 and collected at head unit 121 through a third line 128. All of the NO x gaseous process vent streams 128, after being combined at head unit 121, are fed to conduit 129 for mixing with air with this mixed stream being fed to a packed bed unit 130 for contact with water 131 to form dilute or weak nitric acid. The weak nitric acid is recycled through line 132 to nitric acid feed stock line 104. Clean NO x free vent gas is vented from the packed bed through line 134.
  • the NO x abatement/acid production unit 130 is shown as two separate packed bed sections 30 and 40.
  • the lower packed bed section 30 receives the NO x gases mixed with air through line 129 and water 131.
  • the NO x gases, water and air at a pressure of 2 to 5 atmospheres are circulated through packed bed 30 and recovered as weak nitric acid at 132 which is recycled and used as nitric acid stock.
  • This unit will recover approximately 98% of the NO x gases as weak nitric acid in unit 30.
  • Increased pressure favors increased recovery.
  • a heat exchanger generally at 32 on unit 30 maintains the temperature in unit 30 as low as possible favoring acid production.
  • the second or upper section 40 is used for clean up of the tail gases from first section 30.
  • the second section is a shorter section and is irrigated either with circulating water or caustic.
  • caustic is not used in that it will be consumed by CO 2 .
  • This section receives NO x tail gases from section 30 at conduit 32 and removes residual NO x gases to give a colorless stack gas discharged at 42.
  • the second bed may be either eliminated or, if it is operated with water, may feed to the first bed.
  • the liquid effluent is combined with other weak processing effluents for recycling through line 132.
  • the packed bed sections are operated at pressures which vary from 2 to 5 atmospheres as above stated. Typically, the weak nitric acid formed for recycling will vary in strength from 2 to 10 weight percent, depending upon the requirements of the process.
  • the NO x collection will be carried out at the temperature and pressure of the nitrating process.
  • the pressure in the unit for forming dilute nitric acid will preferably be at an elevated pressure selected to accommodate most efficient formation of nitric acid under the other conditions of the nitrating process.

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
  • Treating Waste Gases (AREA)
  • Glass Compositions (AREA)
  • Processing Of Solid Wastes (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Abstract

A continuous process to nitrate a nitratable aromatic compound utilizing nitric acid and sulfuric acid feed stocks is described. The process includes the collecting of NOx gases produced in the nitrating process and treating the NOx gases with water under pressure to produce weak nitric acid which is recycled to the nitric acid feed stock. The process is efficient, permitting the venting of NOx free gases to the atmosphere.

Description

FIELD OF INVENTION
This invention relates to an improved continuous process for the nitration of nitratable organic compounds and particularly for the preparation of mononitrobenzene (MNB) from benzene utilizing nitric acid and sulfuric acid feed stocks. According to the improved nitration process, nitrous oxide (NOx) gases produced in the nitration process are collected in water under pressure to produce weak nitric acid which is recycled to the nitric acid feed stock.
BACKGROUND OF INVENTION
Nitrated aromatic hydrocarbons and nitrated halogenated aromatic hydrocarbons and particularly mononitrobenzene are important chemical intermediates. Guenkel et al, United States Patent No. 5,313,009 (the '009 patent), assigned to the assignee of the present invention, describes a continuous process to nitrate a nitratable aromatic compound, typically an aromatic hydrocarbon or a halogenated aromatic hydrocarbon, and particularly benzene, in which the formation of oxidation by-products is substantially reduced compared with the prior art and wherein the reaction rate is substantially increased. The disclosure of this patent, in its entirety, is incorporated herein by reference. According to the process of the '009 patent, NOx gases are still formed which preferably are not released into the atmosphere for environmental reasons. The prior art has suggested treating these NOx gases with a caustic solution to form sodium nitrite or sodium nitrate salts, which are disposed of as the salt. Small quantities of CO2 are also formed in the nitration process. CO2 will react with sodium hydroxide to form sodium carbonate; this increases the consumption of sodium hydroxide. Further, the use of sodium hydroxide and formation of salts which must be subsequently disposed of is not completely acceptable on an industrial basis. The discharge of nitrates and especially nitrites of sodium is facing increasingly strict regulation.
The present invention describes a system for removal of NOx gases which can be utilized in conjunction with the nitration process disclosed in the aforesaid '009 patent, as well as other nitration processes where NOx gases are formed to efficiently and effectively convert the NOx gases into weak nitric acid, preferably recycled to the nitric acid feed stock.
SUMMARY OF INVENTION
The present invention provides a continuous nitration process of an aromatic compound such as benzene utilizing nitric acid and sulfuric acid feed stocks wherein NOx gases produced in the process are contacted with water under pressure and converted to weak nitric acid which is recycled to the nitric acid feed stock. According to the improved process of the invention, NOx gases are collected from strategic areas of the nitrating system, contacted with air and water, for example, in a packed bed unit at elevated temperature and pressure whereby the NOx gases are absorbed by the water to form weak nitric acid. The weak nitric acid is recovered from the packed bed unit and recycled to the nitric acid feed stock. CO2 is not absorbed in a NOx scrubber if the scrubber is operated in an acidic mode. Clean NOx free vent gas is vented from the packed bed unit. The system is not only effective and efficient, but additionally is cost saving in that the NOx gases being recovered as nitric acid are reused in the nitration process.
Having described the invention in general terms, the presently preferred embodiment will be described in reference to the drawing.
BRIEF DESCRIPTION OF THE DRAWINGS
In the drawings,
  • FIGURE 1 diagrammatically illustrates a continuous nitrating process carried out in the adiabatic mode, as described in the '009 patent, utilizing the NOx recovery system of the present invention, and
  • FIGURE 2 illustrates two separate but interconnected packed bed sections utilized in contacting the NOx gases with water to form and concentrate nitric acid for recycling.
DETAILED DESCRIPTION OF PREFERRED EMBODIMENT
Referring to Figure 1, a nitration process operating under adiabatic conditions as disclosed in the '009 patent is illustrated. A pipe nitrator 100 receives concentrated sulfuric acid from conduit 102, nitric acid from conduit 104 and hydrocarbon, i.e., benzene, to be nitrated from conduit 106. The acid streams are blended in a ratio such that the resulting mixed acid contains nitric acid mostly in the form of reactive species, i.e., the nitronium ion as described in the '009 patent. The two acid streams from conduits 102 and 104 may be mixed in line before entering the pipe nitrator 100 or they may be introduced separately into the pipe nitrator 100. The pipe nitrator 100 discharges to a stirred tank type nitrator 112. In cases where the reaction rate is very fast, which is specific to the hydrocarbon species to be nitrated and specific to the operating conditions, the reaction may go essentially to completion inside the pipe nitrator 100 so that the stirred tank type of nitrator 112 is not required. In cases where the nitration rate is slow, the pipe nitrator 100 serves mainly as a hydrocarbon dispersion device. Fresh nitrating acid enters the stirred tank nitrator 112 and intimately mixes with fresh hydrocarbon. The process fluids pass to a separator 114 and the nitro product compound is discharged from separator 114 through conduit 116 and fed to a product wash and effluent treatment system 124. Pure nitro organic product, i.e., mononitrobenzene when benzene is treated, is recovered at conduit 125, aqueous effluent is discharged through conduit 126 and some organic recycle is fed by line 127 to hydrocarbon feed 106.
Spent sulfuric acid recovered from separator 114 is delivered to a sulfuric acid concentrator 118. In the sulfuric acid concentrator 118 water is removed via conduit 120 which is fed to a vacuum system 123 while reconcentrated sulfuric acid is recycled to the pipe nitrator 100 through conduit 117.
NOx gases are drawn off in vacuum system 123 and collected through line 128 at head unit 121. Condensate from vacuum system 123 is fed to product wash and effluent treatment system 124 where additional NOx gases are drawn off and fed to head unit 121 through a second line 128. Finally, additional NOx gases are vented from separator 114 and collected at head unit 121 through a third line 128. All of the NOx gaseous process vent streams 128, after being combined at head unit 121, are fed to conduit 129 for mixing with air with this mixed stream being fed to a packed bed unit 130 for contact with water 131 to form dilute or weak nitric acid. The weak nitric acid is recycled through line 132 to nitric acid feed stock line 104. Clean NOx free vent gas is vented from the packed bed through line 134.
As shown in Figure 2, the NOx abatement/acid production unit 130 is shown as two separate packed bed sections 30 and 40. The lower packed bed section 30 receives the NOx gases mixed with air through line 129 and water 131. The NOx gases, water and air at a pressure of 2 to 5 atmospheres are circulated through packed bed 30 and recovered as weak nitric acid at 132 which is recycled and used as nitric acid stock. This unit will recover approximately 98% of the NOx gases as weak nitric acid in unit 30. Increased pressure favors increased recovery. A heat exchanger generally at 32 on unit 30 maintains the temperature in unit 30 as low as possible favoring acid production. The second or upper section 40 is used for clean up of the tail gases from first section 30. The second section is a shorter section and is irrigated either with circulating water or caustic. Preferably, caustic is not used in that it will be consumed by CO2. This section receives NOx tail gases from section 30 at conduit 32 and removes residual NOx gases to give a colorless stack gas discharged at 42. Depending upon the discharge requirements, the second bed may be either eliminated or, if it is operated with water, may feed to the first bed. The liquid effluent is combined with other weak processing effluents for recycling through line 132. The packed bed sections are operated at pressures which vary from 2 to 5 atmospheres as above stated. Typically, the weak nitric acid formed for recycling will vary in strength from 2 to 10 weight percent, depending upon the requirements of the process. Thus, in the aforesaid system, the NOx collection will be carried out at the temperature and pressure of the nitrating process. However, the pressure in the unit for forming dilute nitric acid will preferably be at an elevated pressure selected to accommodate most efficient formation of nitric acid under the other conditions of the nitrating process.
As will be apparent to one skilled in the art, although the present invention is described with the specific process disclosed in the '009 patent, it can be used in any of the known prior art nitrating systems where nitration is accomplished with nitric acid and sulfuric acid feed stocks and NOx gases are formed. Other nitrating systems are described in the '009 patent under the heading "Description of the Prior Art." As will also be apparent to one skilled in the art, the NOx gases, depending upon the particular system employed, may be recovered at various points in the nitration system. While the NOx gases are converted to nitric acid in a packed bed system, as above described, other systems can be utilized, it only being essential that the NOx gases are brought into contact with water, preferably under pressure, so as to form weak nitric acid. These modifications, being known to one skilled in the art, are to be covered by the appended claims.

Claims (8)

  1. A continuous process to nitrate a nitratable aromatic compound comprising:
    a) introducing a nitratable aromatic compound, nitric acid and sulfuric acid into a nitrator;
    b) reacting said nitratable aromatic compound, nitric acid and sulfuric acid under controlled conditions to produce a nitrated aromatic compound and NOx gases;
    c) separating said NOx gases from said nitrated aromatic compound;
    d) contacting said NOx gases with water under pressure to form weak nitric acid, and
    e) recycling said nitric acid for reuse in the process.
  2. The process of claim 1 wherein said nitratable aromatic compound is benzene and the nitrated aromatic compound is mononitrobenzene.
  3. The process of claim 2 wherein said NOx gases are contacted with water under pressure in a packed bed system.
  4. The process of claim 3 wherein said packed bed system comprises two separate but connected packed beds.
  5. A nitration system comprising a nitrator for nitrating a nitratable aromatic compound, including feed means for feeding each of a nitratable aromatic compound, nitric acid feed stock and sulfuric acid feed stock into said nitrator; separator means for separating a nitrated aromatic compound from spent sulfuric acid; means for separating NOx gases from said nitrated aromatic compound, and means for contacting said NOx gases with water to form weak nitric acid.
  6. The nitration system of claim 5 wherein said nitratable aromatic compound is benzene.
  7. The nitration system of claim 6 wherein said nitrator further includes a product wash and effluent system and means for separating and collecting NOx gases therefrom.
  8. The nitration system of claim 7 wherein said nitrator further includes a vacuum system for receiving nitrated aromatic compound and water and means for separating and collecting NOx gases therefrom.
EP99114369A 1998-07-30 1999-07-21 Improved nitration process Expired - Lifetime EP0976718B1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US126087 1987-11-30
US09/126,087 US5963878A (en) 1998-07-30 1998-07-30 Nitration process

Publications (3)

Publication Number Publication Date
EP0976718A2 true EP0976718A2 (en) 2000-02-02
EP0976718A3 EP0976718A3 (en) 2000-12-27
EP0976718B1 EP0976718B1 (en) 2003-03-12

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EP99114369A Expired - Lifetime EP0976718B1 (en) 1998-07-30 1999-07-21 Improved nitration process

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EP (1) EP0976718B1 (en)
AT (1) ATE234272T1 (en)
DE (1) DE69905811T2 (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2012160072A1 (en) 2011-05-24 2012-11-29 Basf Se Process for preparing polyisocyanates from biomass
WO2014016289A1 (en) 2012-07-27 2014-01-30 Bayer Materialscience Ag Method for producing nitrobenzene by adiabatic nitriding
US8697913B2 (en) 2009-06-17 2014-04-15 Huntsman International Llc Chemical installation
US8933262B2 (en) 2011-05-24 2015-01-13 Basf Se Process for preparing polyisocyanates from biomass
US9260377B2 (en) 2012-07-27 2016-02-16 Bayer Materialscience Ag Method for producing nitrobenzene by adiabatic nitriding
US9284256B2 (en) 2012-07-27 2016-03-15 Bayer Materialscience Ag Process for the production of nitrobenzene by adiabatic nitration
WO2020212333A1 (en) 2019-04-17 2020-10-22 Covestro Deutschland Ag Process for the continuous production of nitrobenzene
WO2020212334A1 (en) 2019-04-17 2020-10-22 Covestro Deutschland Ag Process and device for producing nitrobenzene

Families Citing this family (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4485731B2 (en) 2000-03-02 2010-06-23 ダウ グローバル テクノロジーズ インコーポレイティド Tubular reactor, process for conducting liquid / liquid multiphase reaction in tubular reactor and process for ring nitration of aromatic compounds in tubular reactor
JP3635026B2 (en) * 2000-06-14 2005-03-30 株式会社サンテックシステム Sulfuric acid recycling equipment
DE10047163A1 (en) * 2000-09-22 2002-04-11 Basf Ag Process for the nitration of aromatic hydrocarbons
SG119142A1 (en) * 2000-11-21 2006-02-28 Suntec System Co Ltd Sulfuric acid recycle apparatus
US9227909B2 (en) 2012-10-10 2016-01-05 Covestro Deutschland Ag Method for the continuous production of nitrobenzene
WO2016050759A1 (en) 2014-10-02 2016-04-07 Covestro Deutschland Ag Exhaust gas cleaning in a method for continuously producing dinitrotoluene
DE102017110084B4 (en) 2017-02-03 2019-07-04 Josef Meissner Gmbh & Co. Kg Process and plant for the adiabatic nitration of aromatics
DE102018217955B4 (en) * 2018-10-19 2020-06-04 Plinke Gmbh Process for working up mixed acid and waste water from the nitration of aromatics and device for carrying out the process
CN110511146A (en) * 2019-09-17 2019-11-29 四川北方红光特种化工有限公司 The production method and its production system of a kind of low single nitro ortho-xylene of waste acid quantity
EP4648884A1 (en) 2023-01-09 2025-11-19 Basf Se Process for removing nitric oxide, nitrous oxide and carbon monoxide from a gas stream
WO2025125207A1 (en) 2023-12-11 2025-06-19 Basf Se Process for removing nitrogen monoxide, nitrogen dioxide and nitrous oxide from an exhaust gas stream

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2453846A1 (en) * 1979-04-10 1980-11-07 Azote & Prod Chim PROCESS AND PLANT FOR MANUFACTURING NITROPARAFFINS BY NITRATION OF HYDROCARBONS IN THE GASEOUS PHASE
DE2921487C2 (en) * 1979-05-26 1984-11-08 Josef Meissner GmbH & Co, 5000 Köln Process for the removal of volatile aromatic compounds
DE19512114C2 (en) * 1995-04-04 2000-04-27 Meissner Gmbh & Co Kg Josef Recovery of nitric acid from nitriding processes

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8697913B2 (en) 2009-06-17 2014-04-15 Huntsman International Llc Chemical installation
US9102586B2 (en) 2009-06-17 2015-08-11 Huntsman International Llc Method for producing DADPM
WO2012160072A1 (en) 2011-05-24 2012-11-29 Basf Se Process for preparing polyisocyanates from biomass
US8933262B2 (en) 2011-05-24 2015-01-13 Basf Se Process for preparing polyisocyanates from biomass
WO2014016289A1 (en) 2012-07-27 2014-01-30 Bayer Materialscience Ag Method for producing nitrobenzene by adiabatic nitriding
US9260377B2 (en) 2012-07-27 2016-02-16 Bayer Materialscience Ag Method for producing nitrobenzene by adiabatic nitriding
US9284255B2 (en) 2012-07-27 2016-03-15 Bayer Materialscience Ag Method for producing nitrobenzene by adiabatic nitriding
US9284256B2 (en) 2012-07-27 2016-03-15 Bayer Materialscience Ag Process for the production of nitrobenzene by adiabatic nitration
WO2020212333A1 (en) 2019-04-17 2020-10-22 Covestro Deutschland Ag Process for the continuous production of nitrobenzene
WO2020212334A1 (en) 2019-04-17 2020-10-22 Covestro Deutschland Ag Process and device for producing nitrobenzene

Also Published As

Publication number Publication date
DE69905811D1 (en) 2003-04-17
EP0976718A3 (en) 2000-12-27
EP0976718B1 (en) 2003-03-12
DE69905811T2 (en) 2003-11-13
US5963878A (en) 1999-10-05
ATE234272T1 (en) 2003-03-15

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